The document outlines a stewardship management plan for Sallas Forest on Sidney Island, focusing on the protection and sustainability of its diverse forest ecosystems from 2013 to 2018. The plan includes clear objectives for forest management, emphasizing the promotion of growth, biodiversity, and aesthetic values while addressing challenges such as deer overpopulation and fire hazards. The management strategy categorizes the forest into distinct types based on age and management objectives, guiding specific actions necessary for maintaining the health of the forest ecosystem.

1. STEWARDSHIP OF SIDNEY ISLAND’S FOREST
A Management Plan
Prepared by
Peter H. Pearse, R.P.F. (ret)
for the
Ecological Stewardship Committee
SALLAS FOREST STRATA CORPORATION
January 2013

2. Contents
Page
A Stewardship Plan for Sallas Forest
1
Objectives
1
The Forest
2
The Main Forest Types
6
Special Purpose Forest Types
10
Management Priorities
13
Other Components of the Plan
19
Financial Implications
22
Beyond 2017
22
Annex: Stewardship of Sidney Island’s Natural Resources:
Objectives and Guidelines

3. STEWARDSHIP OF SIDNEY ISLAND’S FOREST
A Management Plan
A Stewardship Plan for Sallas Forest
Sidney Island’s landscape is dominated by forest. This impressive forest, varying from oak
meadows to deep coastal timber, contributes a great deal to the island’s unique appeal. Sallas
Forest Strata Corporation is committed to managing its forest and other natural resources with a
view toward protecting and sustaining them and the natural ecosystems they support.
Because forests take a long time to grow, forest management calls for long-term planning. In the
case of Sallas Forest, where forest management is delegated to a committee, explicit plans are
also needed to keep the strata council and owners informed and engaged, and to facilitate
financial planning and accountability. This document presents a forest stewardship plan for the
next five years, 2013 to 2018, designed to advance the strata corporation’s broad, long-term
objectives for the island’s environment and natural resources.
Objectives
A coherent management plan must be based on clear objectives. In the present case, the
objectives and priorities to be adopted are clearly specified in Stewardship of Sidney Island’s
Natural Resources: Objectives and Guidelines, a document approved for this purpose by the
strata council in September 2011. This document elaborates on specifications in the strata
corporation’s Statutory Building Scheme, which is binding on all owners, and makes it clear that
the primary objective is to protect and maintain the island’s forest and ecosystems in their
natural, healthy condition. Also to be considered in managing resources are aesthetic and
recreational values and the privacy of owners.
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4. The Objectives and Guidelines document refers to several other objectives relevant to forest
management, including development of the “park-like” character of forest and meadows and
their accessibility for the enjoyment of owners, restoration of disturbed landscapes and
protection of rare and endangered species. And, with the important caveat that resources are not
to be exploited primarily for financial gain, the guidelines prescribe that when resource products
such as venison and timber are harvested or removed for other management purposes, any
commercial value they may have should be recovered through sale to owners or others.
These stewardship objectives and guidelines are attached as an Annex to this report. They
provide the framework for the forest stewardship plan described in the following pages. But it is
important to note that forest management plans must respond to other constraints as well, such as
the myriad laws and regulations of governments that bear on activities on Sidney Island, the
strata corporation’s Statutory Building Scheme and its limited financial resources.
This forest management plan is unusual in two respects; one is that its objectives, noted above,
are different and more complicated than those of most private and governmental forest owners
who are primarily concerned with commercial forest production. The second is that it is written
for readers, especially owners of the strata corporation, who need clear information about
proposed silvicultural activities and their implications without the usual arcane terminology and
presumptions of foresters and ecologists. This has required simplification of information about
the forest itself and more explanation of forest management techniques.
The Forest
The forest, as this term is used here, is the strata corporation’s common property not devoted to
other purposes, but it includes some open bluffs and meadows. As Figure 1 shows, it occupies
472 hectares, two-thirds of Sallas Forest land, and an area larger than Vancouver’s Stanley Park.
Some special features of this forest provide context for the proposed plan.
Sidney Island is in the heart of the coastal Douglas fir zone, and this impressive species
dominates the island’s forest. In much lesser abundance other species common in coastal forests
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5. are mixed with the Douglas fir, notably the coniferous western red cedar and grand (or balsam)
fir, and the deciduous red alder and bigleaf maple. In addition to these, the island’s forest
supports a remarkable variety of relatively rare species such as the picturesque arbutus, Garry
oak, Pacific dogwood and western yew. Still others, such as black cottonwood and trembling
aspen, are unusual on the Gulf Islands. This range of tree species, coupled with the island’s
diversity of other vegetation, topography and wildlife, gives the forest its special interest and
attraction. [For excellent illustrations and descriptions of all these species, see Tree Book Index Ministry of Forests.]
The present forest has been shaped by two broad influences. One is the island’s natural growing
conditions – its geological foundation, climate and fertility, which determine the natural
composition of species in the forest. The other is the history of forest disturbance. In its preEuropean settlement wilderness, the Douglas fir forest depended for its regeneration on
intermittent forest fire to clear away the forest canopy and stimulate regeneration of a new forest,
resulting in forest stands in which the trees over broad areas were all more or less the same age.
Over the last century, clear-cut logging had a similar effect. And over the last three decades,
artificial reforestation, thinning, fertilization and other silvicultural activities have significantly
influenced the structure of the present forest.
Over the past century, almost all the forest has been disturbed by logging, most of which
occurred in three episodes: the first, during World War I, removed some of the huge original oldgrowth Douglas fir and cedar trees; the second, shortly after World War II, removed most of the
remaining old growth; the third, in the 1980s, removed much of the then 60- to 70-year-old
second growth that had established itself where the first phase of logging had taken place. For
the most part, the areas logged were quickly reforested naturally or through planting, so that
much of the present forest consists of even-aged stands of an age dating from one of these three
episodes.
For decades the forest has suffered from the depredations of fallow deer, introduced to the island
early in the last century. Apart from the resulting disruption of the whole forest ecosystem, the
overpopulation of deer made reforestation difficult, expensive and often unsuccessful. Over the
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6. last four years, impressive progress has been made in reducing and controlling the deer
population, with significant benefits in lower cost and higher success of reforestation efforts.
The major threat to the forest is fire. The strata corporation supplements the provincial
government’s fire suppression program and facilities with its own fire regulations, equipment
and voluntary Fire Team. A variety of pests also affect the forest, most conspicuously an insect
that defoliates mature balsam trees, a fungus that infects and kills arbutus trees, and another that
attacks the roots of Douglas fir, resulting in patches of dead or dying trees of that species. But
these are normal in the forests of this region, and are minor threats to the island ecosystem
compared to the formerly hyperabundant fallow deer.
Today, the forest is generally healthy, and thanks to the natural fertility of the land and an
aggressive reforestation program over the last couple of decades, it is, in large part, growing
vigorously.
It will help in understanding later discussion in this document to be more specific about this
growth. Foresters measure wood in cubic metres (a cubic metre being roughly the amount of
wood contained in a typical utility pole). Our data indicate that the forest is currently adding
biomass in the form of wood at an average rate of at least five cubic metres per hectare per year,
or a total of some 2,360 cubic metres annually.
Sidney Island’s forest is best understood as an ecosystem in the long, slow process of restoration
following removal of the original old growth – the stands of differing ages marching through the
age classes from seedlings to maturing forest – a process hastened in recent decades by
reforestation, other silvicultural measures and aggressive control of the deer population. The
management plan presented here is intended to further advance the process of restoration of the
forest ecosystem and its environmental and other benefits to Sallas Forest owners.
4

7. Figure 1. Sallas Forest Land Use
More specifically, our Objectives and Guidelines imply that the forest should be managed to
promote the forest’s growth and vigour, its biodiversity and its aesthetic and recreational values.
Aesthetic quality, being a matter of individual taste, is particularly difficult to define and
measure, but studies show that people generally appreciate old and big trees more than young
and small ones, relatively open groves more than dense stands, and variety more than
homogeneity – preferences that are commonly reflected in parks and are assumed to apply here.
5

8. The Main Forest Types
Forest planning depends critically on data about the forest itself – the species composition, age,
density, rate of growth and other characteristics of the forest cover. Our information about the
forest is based mainly on an inventory undertaken in 1998 by a forestry consulting firm retained
by the strata corporation’s predecessor, Sallas Forest Limited Partnership. In important respects
these data are now out of date, but with extrapolations, information gleaned from other sources,
adjustments based on personal knowledge and tolerance for margins of error, it provides an
adequate base of information for present purposes.
For practical management planning, it is helpful to divide the forest into categories, each of
which calls for a distinctive management prescription. To meet Sallas Forest’s criteria for
management, the categories identified here have been selected according to two considerations.
One is the characteristics of the forest itself. Because the Douglas fir forest usually grows in
even-aged stands, and the age of stands determines the kind of silvicultural measures they need,
the forest has been classified into forest types defined by the age of the trees.
The second consideration is the strata corporation’s particular management objectives in
different parts of its property. Since forests can be managed for a variety of purposes, and the
strata corporation’s purposes and priorities differ in different parts of the island, this must also be
considered in designing the overall management regime.
Thus the forest has been classified into 10 Forest Types, based on the age of the trees and the
strata corporation’s varying objectives and priorities, which together largely determine the
appropriate management regime for each. These forest types, described below, are shown on the
colour-coded map in Figure 2. This map can be viewed at higher resolution and with more detail
on the Sidney Island website (Map of Sidney Island’s Forest Cover and Inventory).
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9. Naturally Open Areas
The common property contains some 44 hectares of Naturally Open Areas in the
form of rocky knolls, meadows and wetlands, coloured yellow in Figure 2. These
areas lack a continuous forest cover (though they may contain scattered trees and
shrubs). Apart from the use of some meadows in deer operations, the objective in
managing these areas is to preserve them in their natural condition and to protect
their aesthetic and recreational qualities.
New Forest
New Forest refers to forest land on which the forest has been removed or
disturbed, the new plantation is less than 10 years old, and reforestation remains
either inadequate or in need of maintenance. As a result of past reforestation
efforts, the area that still requires planting has been substantially reduced to less
than two hectares. This, and another 29 hectares planted recently (very pale green
in Figure 2), requires continuing protection from deer for a few more years. The
management objective for these areas is to bring them to a reforested, freegrowing stage as soon as is practicable.
Juvenile Forest
Juvenile Forest, light green in Figure 2, consists of stands between 10 and 35
years old, covering 210 hectares, more than any other forest type. The juvenile
phase of a forest is the period in which silvicultural measures are most effective in
shaping the future forest and maintaining its growth and vigour. The most
important of these measures for present planning purposes are “spacing,” the
removal of superfluous, smaller trees that inhibit the growth of the ultimate stand;
and “pruning,” the removal of lower, usually dead branches that impair aesthetic
and recreational values and create a fire hazard. The small trees removed in
spacing operations have no commercial value, but are left on the forest floor to
decay and contribute nutrients to the remaining trees.
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10. Mid-aged Forest
Stands between 35 and 50 years old, referred to as Mid-aged Forest, cover 31
hectares, coloured middle green in Figure 2. This age bracket is a period of rapid
growth and development of the forest.
Maturing Forest
Maturing Forest, occupying 156 hectares of Sallas Forest (coloured dark green in
Figure 2), is composed of trees more than 50 years old. At this age, stands can be
thinned to the density desired for the mature forest. In Sallas Forest, where the
stands now more than 50 years old were spaced, pruned and fertilized in their
juvenile phase, thinnings usually have commercial value and can be recovered
and sold.
8

11. Figure 2. Forest Types in Sallas Forest
Note: This map is available at higher resolution at www.sidneyisland.ca (Map of Sidney Island’s
Forest Cover and Inventory)
9

12. Special Purpose Forest Types
The remaining forest types refer to parts of the common-property forest which must be managed
to respond to special priorities in particular areas.
Conservancies
Conservancies occupy 55 hectares of the common property, mostly around the
southeast end of the island, coloured buff in Figure 2. The covenants over these
areas, held by the Islands Trust, restrict the strata corporation’s activities on these
lands and define the management objective as conservation. Thus the strata
corporation’s management activity is reduced to protecting these areas from
disturbance.
Roadsides
Roadsides here refer to forest land on common property within 10 metres of the
edge of main or graveled roads. Roadsides must be managed with particular
attention to three objectives. First, they must contribute to the safety of vehicular
traffic by removal of physical obstructions and maintenance of sightlines. Second,
since most forest fires start on or near roads, roadsides must be managed to
minimize fire hazard. Third, because the roadways are so important to the island’s
general appearance, roadsides must be managed with special attention to their
aesthetic qualities. Fortuitously, these three priorities call for complementary
management prescriptions; removal of obstructive trees, wide spacing, pruning
and grooming of trees, and removal of debris. About 30 hectares fall within these
roadsides on common property.
Firebreak
The strata corporation’s Fire Team has initiated construction of a firebreak, 10 to
15 metres wide, along the south side of Sallas Lane and extending across the
island from Hamley Point to the southwest shore. Within this strip the brush,
debris, surface duff and some trees have been removed, which, combined with the
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13. adjacent road, forms a barrier to the spread of wildfire from the high-risk southern
part of the island. This Firebreak, which occupies more than two hectares, is yet
to be completed and trees within it must be spaced and pruned.
Residential Adjacencies
Residential Adjacencies refers to common-property forest within 10 metres of
residential lots, which amounts to some six hectares. Because of the implications
for the owners’ privacy and the forest’s effect on the aesthetic quality of their
residential environment, adjacent forest areas must be managed with a view
toward protecting these values, which usually implies maintaining a relatively
dense and vigorous screen of forest where that is feasible.
Disturbed Landscapes
Disturbed Landscapes are areas where the forest has been removed and the
surface of the land has been disturbed, as in the case of gravel pits and quarries,
which occupy nearly four hectares. The management objective is to restore these
areas when they are no longer used, which often calls for some landscaping as
well as reforestation.
Table 1 provides a summary of these Forest Types, their characteristics and management
requirements. The 10 types are, of course, a simplification of the full variety of forest conditions
in Sallas Forest, because every hectare differs. But they serve to aggregate and distinguish the
parts of the forest that call for particular management measures referred to in Table 1 and
discussed further below.
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14. Table 1. Forest Types and their management priorities
Management
Priorities
Management
Techniques
Area
(ha)
Forest Type
Characteristics
Naturally open areas
Meadows, knolls, wetlands
Conservation,
aesthetics, wildlife
management
Primarily protection
44.5
New forest
Inadequately stocked forest
and plantations less than 10
years old
Reforestation
Planting and plantation
maintenance
31.1
Juvenile forest
Plantations 10 to 35 years old
Stand composition,
growth & development
Tree spacing and pruning
Mid-aged forest
Stands between 35 and 50
years old
Forest health, diversity,
aesthetics
General forest
maintenance
Maturing forest
Stands more than 50 years old
Biodiversity, aesthetics
Thinning, fire hazard
control and promotion of
old-growth characteristics
Main Forest Types
Total Main Forest Types
209.9
30.7
155.7
471.9
Special Purpose Forest Types
Conservancies
Management constrained by
covenants
Conservation
Protection
55.4
Roadsides
Vegetation within 10 m of
roads
Traffic safety,
aesthetics, fire control
Vegetation & debris
removal and tree grooming
30.2a
Firebreak
Forest bordering road serving
as firebreak
Fire-hazard abatement
Spacing & pruning of trees
and debris removal
2.4a
Residential adjacencies
Forest within 10 m of
residential lots
Privacy, aesthetics
Maintenance of robust
forest
5.7a
Disturbed landscapes
Gravel pits, quarry
Restoration
Surface landscaping and
reforestation
3.7
Total Special Purpose Forest Types
97.4
Non-forested Areas
Water and wetland
Ponds and wetland
2.6
Roads and other
Road surfaces, parking lots, air strip and hunter’s cabin
27.6
Total Non-forested Areas
Total Common Property
a
This area is included in the area of Main Forest Types above
12
30.2
561.1

15. In addition to the above forest types, Table 1 shows, for completeness in accounting for land use,
two categories of Non-forested Land shown on the accompanying map, Water and wetland and
Roads and other. These are not managed forest and are not considered further in the following
discussion, but together they amount to about 30 hectares that, when added to the forest types
described above, account for all of the 561 hectares of common property. With these exclusions,
the forest management plan applies to the strata corporation’s common property, the
management of which is the responsibility of the corporation itself through the strata council.
Also excluded from discussion, and from Table 1, are the 154 hectares of private residential lots
around the perimeter of the island, which completes the 715-hectare total of all Sallas Forest
land.
It is important to note that although the management measures differ among forest types, they are
designed to contribute, in aggregate, to the overall priority of protecting the forest ecosystem,
and secondarily to the corporation’s other stated objectives.
Management Priorities
The general objective of this five-year plan is to complete the reforestation of areas that have yet
to be reforested and to set all the young stands on a trajectory of healthy growth and
development. Refinements to this general plan, and additional considerations that call for special
measures in particular parts of the forest, are postponed for future plans.
These objectives call for three priorities for the present management plan, as follows.
1. Completion of Reforestation
The first priority is the New Forest, where reforestation remains incomplete. This deserves
attention not only to restore the forest cover but also to do so before competing vegetation
increases the work and cost of doing so.
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16. Consistent with the management priorities outlined above, reforestation should be confined to
areas from which the forest has been removed through logging in years past, not naturally open
areas. The report of the Resource Management Committee to the 2012 annual meeting of the
strata corporation indicated that this inadequately reforested land is now reduced to less than two
hectares, which can be planted and protected in one spring planting program. Accordingly, the
present plan proposes completion of the remaining inadequately reforested areas in the first fiscal
year, i.e. 2013-14.
This, and another 29 hectares of recently planted areas, requires maintenance and protection
from deer for several years, but this requirement will taper off as the young trees grow beyond
the stage at which they are vulnerable to deer and their browse protectors can be removed.
2. Spacing Juvenile Stands
Discussions of forest management, including this one, often refer to increasing or reducing the
density of trees (the number of trees per hectare, or tree spacing) through planting, spacing,
thinning or harvesting. The purpose of planting is obvious, and the rationale for spacing and
thinning is, basically, that as trees grow bigger, the forest can accommodate fewer of them. For
example, a new plantation in a forest like ours is typically planted with 600 to 1,000 seedlings
per hectare (depending on the species, topography and other local conditions). After a couple of
decades, as a juvenile stand, the trees will grow and develop best with roughly half that number
of trees. And by the time they are 50 years old, like our Maturing Forest, the best density is
halved again. Old-growth forests contain even fewer trees per hectare. Spacing and thinning to
enhance growth, and to concentrate growth on the trees that will constitute the mature stand,
significantly hasten development of the forest, leading to an attractive park-like quality of bigger,
well-spaced trees such as those in the upper photo of Figure 3.
In the absence of spacing, the number of trees would diminish through competition; as the trees
grow increasingly dense, their growth will slow and the dominant ones will suppress the others,
which then gradually die and fall. But this process takes much longer – a century or more. And,
significantly for Sallas Forest, this alternative does little to bolster the forest’s health and vigour,
14

17. its aesthetic and recreational values, or its park-like character. Moreover, the accumulation of
dead trees, dry lower branches and debris in untreated stands leaves them much more vulnerable
to fire.
In some circumstances, even in areas reforested by planting, natural seeding following fire or
logging produces a prolific growth of seedlings that can stagnate growth of the young stand.
Some such areas in Sallas Forest are already so dense and entangled that they are almost
impenetrable and should be spaced without further delay. Apart from the adverse effect of such
congested stands on the forest’s growth, the longer such spacing is postponed, the more work
and cost it will entail.
The two photos in Figure 3 illustrate the effect of spacing and pruning. Both were taken on
Sallas Forest lands in forest of similar age and origin. The stand in the upper photo, now part of
the Maturing Forest, was spaced and pruned as a juvenile stand in the 1980s; that in the lower
photo received no treatment. Note the difference in aesthetic and recreational quality, the size
and vigour of the trees, the diversity of vegetation, light penetration and vulnerability to fire.
Because spacing and pruning are so effective in enhancing the forest’s growth, biodiversity,
aesthetic quality and resistance to fire, they deserve high priority for Sallas Forest. And because
so much of Sallas Forest is in its juvenile phase of development when these treatments are most
effective, the provisions for them in the present plan must be substantial.
15

18. Figure 3. The Benefits of Spacing and Pruning. The two photos above were taken in the same
Maturing Forest type and the trees are of similar age. The stand in the upper photo was spaced
and pruned in its juvenile stage; the stand in the lower photo was not.
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19. Both spacing and pruning are labour intensive and costly, and are best programmed over a
number of years. They can be carried out simultaneously or sequentially with spacing first. This
plan proposes spacing all the Juvenile Forest, to the extent that this treatment is needed, over the
five years of this plan, dealing with the oldest and densest stands first, leaving pruning for the
following years.
3. Thinning
The healthy and attractive stands of advanced second growth in the Maturing Forest, shown in
the upper photo in Figure 1, demonstrate the benefits of the spacing and pruning they received in
their juvenile phase in the 1980s. Since then, the trees have grown considerably, closed in, and in
some areas require thinning again to maintain their growth and development.
The trees in the upper photo in Figure 3 are well spaced, but much of the Maturing Forest
contains twice or even three times this density of trees. For example, the largest stand of
overstocked Maturing Forest, surrounding Spar Tree Hill, was spaced to about 600 trees per
hectare about 25 years ago. They have grown vigorously since then, and at their present age and
size, this density is more than double the number of trees that would enable them to maintain
maximum growth and vigour. As the forest becomes increasingly overcrowded, the growth of
trees and other vegetation slows and the biodiversity of the ecosystem narrows. In order to
realize the potential growth and development of the forest, and the additional aesthetic and firehazard control benefits of thinning, the plan proposes thinning a portion of the most overstocked
stands.
However, the special circumstances of Sallas Forest suggest that thinning operations should be
modest in scale and should proceed gradually to minimize visual impacts on the forest and
disturbance to other island activities. Accordingly, to begin, thinning should be planned to
remove no more than 20 per cent of the trees in any area and the total removed should not exceed
500 cubic metres, sufficient to confirm satisfactory arrangements for on-island operations,
contractors and sales.
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20. The extent of overstocking in these stands suggests that the forest would benefit from larger
removals in future, but the present plan proposes a constant level over the five years of this plan.
To put these proposed thinnings in perspective, the forest is growing by at least 2,360 cubic
metres per year, as noted earlier, which is nearly five times the proposed thinning of 500 cubic
metres.
Consistent with our guidelines, we should take advantage of opportunities to recover any
commercial value of trees removed through sale to owners or others, and such opportunities
appear likely. However, past experience has revealed some sensitivity among owners about the
recovery and sale of logs from thinning, and these apprehensions must be considered in planning
new operations.
In 2005 the strata council approved a proposal from the former Resource Management
Committee to carry out modest thinning operations of the kind proposed here and to salvage and
sell any commercially valuable logs that may be recovered. The trees to be removed were
marked and owners were invited to inspect them. The area shown in the upper photo in Figure 3
was posted as a demonstration plot to illustrate the effect of the proposed thinning, and it met
with general approval among owners who inspected it. Several owners nevertheless expressed
concern that too many trees might be removed at once, so the trees were re-marked and the
numbers reduced.
Our most recent thinning projects were in 2006, in which the trees removed were sold to an
owner and milled for house construction on the island, and in 2009 when they were shipped to
Vancouver Island and sold for manufacture into poles. Both were intended to demonstrate the
effects of such operations on the forest. The projects proceeded smoothly, yielding worthwhile
revenue as well as the desired silvicultural benefits, and there was no reported criticism of the
results. The experience demonstrated the importance of advance information and discussion with
owners.
Of course, a project of this kind should be subject to the strata council’s approval of a detailed
financial prospectus, and opportunities to sell thinnings will remain uncertain until a buyer is
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21. secured among owners or elsewhere, which should be explored at least nine months in advance
of any expected operation. It may be appropriate to deposit any revenues from sales of thinnings
in a reserve account for further forest improvement, in keeping with the spirit of the guideline
against utilizing the forest for general financial gain and giving the organizers some flexibility in
shifting forestry work and spending among years.
Other Components of the Plan
A variety of other matters should be incorporated into the forest management plan. Most of these
do not, at this stage, call for special projects, but rather need consideration in carrying out the
activities described above.
Enhancement of Biodiversity
While Sidney Island’s forest supports a considerable variety of tree species, biodiversity of the
forest ecosystem has suffered from past disturbances and excessive populations of exotic deer.
However, the biodiversity of such an ecosystem, an important indicator of its robustness and a
determinant of its aesthetic quality, can be restored through appropriate silviculture, and this
should be an explicit component of forest management plans.
Most importantly, spacing and thinning of the kind described above allows light to penetrate the
forest canopy and stimulates the growth of an understory of other species, especially shadetolerant cedar, balsam and a variety of shrubs. This process is evident on Sidney Island where
roads have opened the forest canopy, promoting the development of an understory in the
roadside forest (visible, for example, along the western side of Greenleaf Lane, south of the
marina). Over time, this understory forms part of the forest canopy, and with the more abundant
shrubbery, results in a more diverse forest ecosystem.
In addition, spacing and thinning can be executed to favour species in low abundance by
removing fewer of them and more of the abundant ones; a technique that can significantly
broaden the species composition of the remaining stands. (Indeed the present predominance of
Douglas fir was exacerbated by the effort of spacing crews in the 1980s, then concerned with
19

22. commercial forestry, to increase the proportion of this most valuable species.) And in the process
of spacing and thinning, snags and dying trees that provide habitat for cavity-nesting birds and
other animals can be preserved.
A third technique to enhance diversity is to create modest open spaces in the forest, which not
only diversifies the forest but also enriches the habitat for wildlife, especially songbirds.
Strategically located open spaces can add significantly to the attraction of forest trails as well.
Some such open spaces already exist. But it will become increasingly important to identify those
that are to be maintained as permanent and where others should be created.
Fire-hazard Abatement
In addition to the strata corporation’s normal precautions and regulations to reduce the threat of
fire, silvicultural operations must be conducted with attention to their particular implications for
forest fire. For example, spacing, thinning and pruning normally reduce the risk of fire by
separating the trees and removing the “ladder fuel” of dry lower branches that can carry ground
fire into the forest canopy. But these operations produce ground debris that can temporarily
elevate the fire hazard. In conducting these operations, it is therefore important to remove debris
back from roads and trails and to ensure that it is flattened to the ground as much as is
practicable to promote its rapid decay. A similar effect, on a much reduced time scale, occurs in
the open meadows, where long summer grass presents a fire hazard, but cutting it and leaving it
on the ground to dry is likely to temporarily aggravate its susceptibility to grassfire.
Pest Control
Special operations to control forest pests and disease of the kind noted above are not warranted,
for the time being at least. However, in the extensive areas proposed for spacing, pruning and
thinning, those operations should be designed to reduce pests to the extent practicable. Thus,
when these activities encounter trees infected with contagious fungi or insects, they should be
removed and properly disposed of.
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23. Coordination
The preceding discussion suggests other opportunities for beneficial coordination of functions
and responsibilities. The spacing of trees in the firebreak, a responsibility of the Fire Team, can
be dealt with in the course of thinning operations. The management of roadside forest overlaps
the Conservator’s responsibility for maintaining the roads. The location of skidroads required in
thinning may affect the trail system, and so on. These circumstances call for consultation among
those concerned to resolve responsibilities for planning, operations and financing. While the
division of responsibilities need not be complicated, it is important that it be clear, and the strata
council should ensure that this coordination take place.
Information Gathering
As noted earlier, this plan is based on information about the forest that is obsolete in important
respects. Particularly worrisome is the inadequacy of information to identify remedial measures
needed, if any, in areas listed in the 1998 inventory as having only sparse numbers of trees. In
addition, while the remaining need for reforestation appears modest, closer examination of the
forest in the course of other work may reveal more areas that need supplementary planting.
During the next five years, this resource information should be brought up to date.
In addition, building on collaborative arrangements with members of UBC’s Faculty of Forestry
initiated in the course of preparing this plan, the strata corporation should sponsor the design of a
dynamic model of Sidney Island’s forest that would enable precise long-term planning in a
format readily accessible and understandable to owners as well as to those responsible for
management.
Participation
Casual observation suggests that management of the forest is a matter of considerable interest to
owners, but they are nevertheless often uncertain and sometimes anxious about management
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24. activities. Henceforth, greater effort should be made to inform owners about the state of the
forest, the management choices available and rationales of management plans.
In addition, opportunities for owners and their families to actively participate in forest
management activities, and their interest and feasibility in doing so, should be explored.
Financial Estimates
Sidney Island raises unique circumstances for forestry contractors, ranging from complications
of transportation and accommodation to the availability of tools, equipment and services, all of
which complicate estimation of the cost of the management activities proposed in this plan.
However, reliable estimates of costs can be obtained from contractors once the scope of work is
decided and approved.
With present information, only a rough indication of the costs of the proposed management
activities is possible but, with this caveat, an estimate of the order of magnitude of the costs
might nevertheless be helpful. Thus, if the silvicultural and other forest management activities
were spread evenly over the next five years, the cost would be in the order of $40,000 per year. If
the thinnings were recovered and sold to owners on the island or to commercial buyers under
typical market conditions, the net cost would be lowered by roughly one-third to half of that
amount.
Beyond 2017
The activities described above are intended to advance, as efficiently as possible over the next
five years, the strata corporation’s objectives for the stewardship of its Sidney Island forest. It is
important to recognize, of course, that this is only a step in an expected continuum of forest
management into the indefinite future.
It is reasonable to assume that the corporation’s objectives for the forest will continue beyond
2018, but by then the condition of the forest will be predictably different as a result of its growth
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25. and the measures taken under this plan. The program proposed here, for the next five years, is
basically one of completing the re-establishment of the forest cover over the same area as that
occupied by the natural forest in the past, and with the same species as those that occurred
naturally. Further, it is designed to set the whole forest on a path of healthy growth and
diversification, consistent with the established objectives of the strata corporation.
It must be acknowledged that it is an ambitious plan, based on an understanding that the strata
corporation seeks a more active forest management program. While it implies a considerable
responsibility for the Ecological Stewardship Committee in organizing, supervising and
coordinating the program of work, the proposed activities, spread over five years, should be
manageable.
The next plan, for the years beginning in 2018, should include a program of pruning the juvenile
stands, as noted above, but beyond that it should shift attention to planning the development of
more particular attributes of the forest. In contrast with the present plan, future planning should
go beyond the usual silvicultural activities for maintaining the forest’s general health and
development to more specific plans for particular parts of the forest, such as the location of open
spaces, and identification of areas that need supplemental planting or rehabilitation. Attention
should be directed as well to strategic issues such as the protection of endangered species, the
control or eradication of exotic plants and animals, the enhancement of rare and attractive trees
such as oak and arbutus, and improvement of access to the forest and its aesthetic qualities.
The more accurate and sophisticated data, mapping and modelling techniques contemplated in
the present plan will facilitate this more detailed planning.
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26. ANNEX